CN106345319B - It is a kind of without support full carbon film of active carbon and its preparation method and application - Google Patents

It is a kind of without support full carbon film of active carbon and its preparation method and application Download PDF

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CN106345319B
CN106345319B CN201610734288.4A CN201610734288A CN106345319B CN 106345319 B CN106345319 B CN 106345319B CN 201610734288 A CN201610734288 A CN 201610734288A CN 106345319 B CN106345319 B CN 106345319B
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active carbon
graphene
carbon film
film
preparation
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CN106345319A (en
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陈宝梁
杨凯杰
朱小萤
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Zhejiang University ZJU
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Zhejiang University ZJU
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Priority to CN201780003007.0A priority patent/CN108136340A/en
Priority to PCT/CN2017/098964 priority patent/WO2018036553A1/en
Priority to US16/328,205 priority patent/US20190176096A1/en
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D71/00Semi-permeable membranes for separation processes or apparatus characterised by the material; Manufacturing processes specially adapted therefor
    • B01D71/02Inorganic material
    • B01D71/021Carbon
    • B01D71/0211Graphene or derivates thereof
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D71/00Semi-permeable membranes for separation processes or apparatus characterised by the material; Manufacturing processes specially adapted therefor
    • B01D71/02Inorganic material
    • B01D71/021Carbon
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/22Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by diffusion
    • B01D53/228Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by diffusion characterised by specific membranes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D67/00Processes specially adapted for manufacturing semi-permeable membranes for separation processes or apparatus
    • B01D67/0039Inorganic membrane manufacture
    • B01D67/0041Inorganic membrane manufacture by agglomeration of particles in the dry state
    • B01D67/00416Inorganic membrane manufacture by agglomeration of particles in the dry state by deposition by filtration through a support or base layer
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D67/00Processes specially adapted for manufacturing semi-permeable membranes for separation processes or apparatus
    • B01D67/0039Inorganic membrane manufacture
    • B01D67/0044Inorganic membrane manufacture by chemical reaction
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D67/00Processes specially adapted for manufacturing semi-permeable membranes for separation processes or apparatus
    • B01D67/0039Inorganic membrane manufacture
    • B01D67/0046Inorganic membrane manufacture by slurry techniques, e.g. die or slip-casting
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D69/00Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor
    • B01D69/02Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor characterised by their properties
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/442Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by nanofiltration
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/444Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by ultrafiltration or microfiltration
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2253/00Adsorbents used in seperation treatment of gases and vapours
    • B01D2253/10Inorganic adsorbents
    • B01D2253/102Carbon
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2253/00Adsorbents used in seperation treatment of gases and vapours
    • B01D2253/30Physical properties of adsorbents
    • B01D2253/302Dimensions
    • B01D2253/308Pore size
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/06Polluted air
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2323/00Details relating to membrane preparation
    • B01D2323/30Cross-linking
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2325/00Details relating to properties of membranes
    • B01D2325/22Thermal or heat-resistance properties
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2325/00Details relating to properties of membranes
    • B01D2325/30Chemical resistance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/283Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/04Disinfection

Abstract

The invention discloses a kind of without support full carbon film of active carbon and its preparation method and application.The full carbon film of active carbon formed is connected as crosslinking agent by graphene, which can be stabilized independently of substrate, while have very high chemically-resistant corrosion resistance and thermal stability.This multi-functional full carbon film has controllable pore structure, and simultaneously for pollutant absorption property with super strength, pore size can be realized to regulate and control from micron order to nanoscale under the regulation of crosslinking agent additive amount and be adjusted.According to above-mentioned property, which can realize the effect of step removal particulate pollutant and small molecule contaminants, can be used for the processing of environmental pollution water body, the fields such as drink water purifying and air cleaning.

Description

It is a kind of without support full carbon film of active carbon and its preparation method and application
Technical field
The invention belongs to field of material preparation more particularly to a kind of without support full carbon film of active carbon and preparation method thereof and answer With.
Background technique
Active carbon is the adsorbent material being most widely used, extensive due to its huge specific surface and abundant pore structure Applied to water body, gas purification, chemical catalysis, the fields such as energy storage.Application referring now to active carbon is often with particulate form Form is added directly in polluted-water and is adsorbed, but this application often will cause the loss of active carbon, be related to simultaneously The time-consuming and laborious separation of solid and liquid process in later period.Also having application is active carbon to be filled in container, or be embedded in poly Carried out in object using.But active carbon packed column is easy contaminated blocking in use, and inlaying for polymer can block Activated carbon pore structure and masking surface texture, influence its absorption property.Meanwhile the fixed active carbon of container or physics of filling Polymer tend not to keep out the erosion and high-temperature operation of chemical substance, limit its application field, so, study and develop Novel active carbon device has a very important significance the application of active carbon.
Summary of the invention
It is an object of the invention to solve problems of the prior art, and provide a kind of without the support full carbon film of active carbon And its preparation method and application, while not only having ensure that its superpower absorption property, but also the ability for making it have particulate matter retention, Extensive space is provided for the application of active carbon.
Since active carbon has huge specific surface area and pore structure abundant, have for dissolved pollutant in water There is superpower absorption property, active carbon has very big application potential in different fields.But since active carbon particle is larger The limitation of size and irregular surface, is difficult between active carbon particle to interact and further device.In order to solve list Weak, the problem of device hardly possible of pure active carbon particle interaction, while high molecular polymer is not introduced, present invention employs one kind Completely new thinking: it using the pi-electron structure of activated carbon surface, is crosslinked with the graphene with armaticity surface as carbonaceous Agent makes particulate form active carbon form a film by the π-π interaction force of active carbon and carbonaceous crosslinking agent surface, is guaranteeing its adsorption energy The ability of its particle entrapment is assigned while power.This multi-functional full carbon film has controllable pore structure, simultaneously for pollution Object absorption property with super strength, pore size can be realized under the regulation of crosslinking agent additive amount to be regulated and controled from micron order to receiving The adjusting of meter level.
The purpose of the present invention is realized particular by following technical scheme:
It is basic material by active carbon without the support full carbon film of active carbon, graphene connects to form active carbon as crosslinking agent Full carbon film.π-π the interaction force of active carbon and carbonaceous crosslinking agent surface makes the formation of particulate form active carbon not need support construction Full carbon film.
Another object of the present invention is to provide a kind of preparation methods without the support full carbon film of active carbon, including following step It is rapid: active carbon being dispersed in water first, active carbon dispersion liquid is formed, adds graphene dispersing solution, and mix well, will mix Solution after even is filtered, and assembles graphene and active carbon in filter membrane substrate, obtains the full carbon film of active carbon.Activity The full carbon film of charcoal can be removed after drying from substrate surface, form independent full carbon film.
Preferably, the size of the active carbon is micron order, it is therefore an objective to make it easier to disperse in water.
Preferably, adjusting pH in alkalinity in active carbon dispersion process.PH preferably controls > 10, has active carbon in water There is stronger electrostatic repulsion (> -30mV), further enhances its dispersibility.
Preferably, the graphene dispersing solution is obtained by graphene oxide dispersion partial reduction.Utilize crosslinking agent Non-covalent bond π between active carbon makes granular activated carbon device be innovative point of the invention with friendship active force, is guaranteeing carbon Under the premise of matter crosslinking agent is fully dispersed in water, restore as far as possible the oxygen-containing extension in its surface can roll into a ball can be enhanced its hydrophobic effect and Surface pi-electron system is conducive to the stability of film forming.
Further, reduction process realizes that partial reduction process is, by the stone in graphene aqueous solution by electronation Black alkene control is controlled in 0.05-0.1mg/ml, pH in 9-12, then carries out heating reduction again.PH value of solution is controlled in 9-12, is protected Stronger electrostatic repulsion between carbonaceous crosslinking agent is demonstrate,proved, keeps it fully dispersed in water, prevents its reunion, pH is preferably 11.Simultaneously Reunion caused by concentration control prevents concentration higher in 0.05-0.1mg/ml
Preferably, the solution after mixing is placed in pressure filter, filtered by the method for pressure filtration by micropore Film substrate film forming.Driving force can be nitrogen in pressure filter, be also possible to other gases, pressure control range is 0.05-0.6Mpa, it is therefore an objective to allow mixed liquor filtering assembling process between shorter within complete (< 30min), prevent the time Too long active carbon dispersion liquid precipitates, and leads to the uneven of film forming.It pressure filter bottom need to be using miillpore filter as base Bottom carries out lamination assembling, filters the miillpore filter substrate of assembling there is no material requirement, function is that retention active carbon and carbonaceous are handed over Connection agent is assembled, but surface is smooth small with activated carbon effect power can be conducive to remove after film forming from substrate surface.
Preferably, the ratio of graphene is adjustable, and the mass ratio of graphene and active carbon is preferred in solution after mixing It is 1%~10%.The thickness of activated charcoal membrane can be regulated and controled by the additive amount of active carbon, and the surface pore structure of activated charcoal membrane can Regulated and controled with the ratio added by carbonaceous crosslinking agent.
The present invention provides a kind of modes of novel absorbent charcoal device, and active carbon is made not add high molecular polymer item It independently forms a film under part, membrane body has superpower pore structure and specific surface area.Implement the film in use to have the advantage that and high score Sub- polymeric membrane is compared, the full carbon film of active carbon chemical stability with super strength and thermal stability.With pure graphene film or carbon nanometer The full carbon film of periosteum is compared, and active carbon has preferable price advantage since preparation cost is cheap.Meanwhile passing through carbonaceous crosslinking agent Additive amount control can the efficient regulation that must realize membrane pores size, it is selective to retain various sizes of particle contamination Object.The study found that the full carbon film of active carbon can be with the microorganism in effectively catching water body, nano particle, and it can efficiently remove depollution Dyes, polycyclic aromatic hydrocarbon, the dissolved pollutants such as heavy metal ion.
It, can be in water body since the full carbon film of active carbon is provided simultaneously with superpower absorption property and controllable pore structure There is very big application potential in the fields such as purification, air cleaning, chemical catalysis or energy reserves.
Detailed description of the invention
Fig. 1 is the electron-microscope scanning figure of full carbon film made from embodiment 1;
Fig. 2 is the electron-microscope scanning figure of full carbon film made from embodiment 3;
Fig. 3 is the electron-microscope scanning figure of full carbon film made from embodiment 5;
Fig. 4 is the electron-microscope scanning figure of full carbon film made from embodiment 7.
Specific embodiment
The present invention is further elaborated with reference to the accompanying drawings and examples, so that those skilled in the art more fully understand Essence of the invention.Reagent or material in the present invention, if being commercial product without specified otherwise.
Graphene dispersing solution preparation:
Graphene dispersing solution is prepared by graphene oxide dispersion partial reduction.Specifically: graphene oxide is configured to Aqueous solution, graphene control makes graphene exist in 9-12 in 0.05-0.1mg/ml, pH control to realize that electrostatic regulates and controls in solution It can be fully dispersed in water.Above-mentioned solution carries out heating reduction 15 minutes at 90 DEG C, obtains graphene oxide dispersion.
Above-described embodiment is preferred embodiment of the invention, and each parameter can be adjusted according to actual needs, simultaneously Graphene dispersing solution directly can also be dispersed to obtain by graphene particles under Action of Surfactant.Or it can also be with Using other graphene dispersing solutions in the prior art.
Embodiment
Film forming procedure of the invention realizes that active carbon and graphene are regulated and controled by electrostatic first before filtering by filtering assembling Keep it fully dispersed in water.Active carbon and graphene dispersing solution are sufficiently mixed with certain proportion, are then added in filter device, So that it is crossed miillpore filter under the action of driving force, and is assembled in miillpore filter substrate surface.Preparation is without support active carbon Specific step is as follows for full carbon film:
(1) active carbon passes through first grinds and passes through 500 mesh screens, guarantees it having a size of micron order.
(2) micron-sized active carbon is added to the water, adjusts solution ph to 11, is regulated and controled using surface electrostatic, in ultrasound Under the action of granular activated carbon is well-dispersed in water, obtain active carbon dispersion liquid.It should be noted that in the step, pH Electrostatic regulating effect can be influenced, when pH controls>10, activated carbon surface electronegativity<-30mV, ultrasonication time are 2min at this time, Guarantee that active carbon particle in water can be fully dispersed.But as long as pH keeps alkalinity, dispersion effect also can be realized substantially.
It (3) will be sufficiently mixed under conditions of the aforementioned graphene dispersing solution prepared and the earthquake of active carbon dispersion liquid and ultrasound It closes, the mass ratio of graphene and active carbon is successively adjusted to 1%, 2%, 3%, 4%, 5%, 6%, 7% in mixed liquor, remembers respectively For 1~embodiment of embodiment 7.
(4) active carbon well-mixed in each embodiment+carbonaceous crosslinking agent mixed liquor is successively placed in pressure filter In, using nitrogen as pressurization gas, pressure limit 0.05-0.6Mpa, miillpore filter substrate aperture is 0.22 substrate, and mixed liquor exists Fast filming in 30min.
(5) it after dry, removes full carbon film to form independent full carbon film from miillpore filter substrate.
Full carbon film resulting to embodiment 1,3,5,7 carries out electron-microscope scanning, and result is as described in Figure 1.In figure, it can see Out, it under the crosslinked action of graphene, is connected with each other, is formed whole as between the active carbon particle of basic material.While with The increase of graphene amount, surface texture gradually become fine and close, pore structure becomes smaller.Meanwhile the thickness of activated charcoal membrane can be with Regulated and controled by the volume that active carbon dispersion liquid adds, addition is more, and film layer is thicker, and the adsorption capacity of film is bigger.
Using the resulting full carbon film of Examples 1 to 7 respectively to chlorella, Escherichia coli, nano silica, nano silver into Row filtering rejection tests.Test result is as shown in table 1, and the activated charcoal membrane of different graphene additive amount ratios has different holes Structure speciality.It, can be with 100% trapped particles having a size of 2 μm when graphene additive amount reaches the 1% of the quality of active carbon Chlorella.It, can be with 100% trapped particles having a size of 1 μm when graphene adding proportion reaches the 2% of the quality of active carbon Escherichia coli.It, can be with 100% trapped particles having a size of 200nm when graphene adding proportion reaches the 3% of the quality of active carbon Nano silica.When graphene adding proportion reaches the 7% of the quality of active carbon, fenestra gap structure be can achieve 24nm, can nano silver with 99.23% trapped particles having a size of 50nm.It can be seen that the pore structure of film can pass through carbonaceous Crosslinking agent adding proportion is adjusted, and crosslinking agent adding proportion is higher, and the pore structure of film is smaller.Full carbon film of the invention can be with Microorganism, nano particle in effectively catching water body.In addition its can be used for removal polluted-water in dyestuff, polycyclic aromatic hydrocarbon, The dissolved pollutants such as heavy metal ion.
Interception capacity of the full carbon film of the different graphene contents of table 1. for particulate matter
Above-mentioned embodiment is only a preferred solution of the present invention, so it is not intended to limiting the invention.Example Such as, although in above-described embodiment, active carbon is obtained after grinding by 500 mesh screens, is not meant to that it must be through 500 mesh screens are crossed, as long as being able to maintain active carbon particle in the micron-scale or even nanoscale, can realize effect of the invention. For another example the case where above-described embodiment only lists, and the mass ratio of graphene and active carbon is 1%~7% in mixed liquor, but pass through Overtesting is adjusted before and after the range, such as mass ratio is 9%, 10% or even 10% or more, also can be realized this hair Bright technical effect, but the properties such as water flux can slightly decline.
It can be seen that those skilled in the art may be used also without departing from the spirit and scope of the present invention To make a variety of changes and modification.Therefore all mode technical solutions obtained for taking equivalent substitution or equivalent transformation, fall Within the scope of the present invention.

Claims (7)

1. a kind of preparation method without the support full carbon film of active carbon characterized by comprising
Active carbon is dispersed in water, active carbon dispersion liquid is formed, adds graphene dispersing solution, and mix well, will mix Solution afterwards is filtered, and assembles graphene and active carbon in filter membrane substrate, obtains the full carbon film of active carbon;It is described Active carbon size be micron order;In active carbon dispersion process, pH is adjusted in alkalinity;The graphene dispersing solution is by aoxidizing Graphene aqueous dispersions partial reduction obtains.
2. the preparation method as described in claim 1 without the support full carbon film of active carbon, which is characterized in that control pH > 10.
3. the preparation method as described in claim 1 without the support full carbon film of active carbon, which is characterized in that partial reduction process In, graphene concentration control in graphene aqueous solution is controlled in 9-12, restored in 0.05-0.1 mg/ml, pH.
4. the preparation method as described in claim 1 without the support full carbon film of active carbon, which is characterized in that the solution after mixing It is placed in pressure filter, is formed a film by the method for pressure filtration by miillpore filter substrate.
5. the preparation method as claimed in claim 4 without the support full carbon film of active carbon, which is characterized in that filtration time < 30 min。
6. the preparation method as described in claim 1 without the support full carbon film of active carbon, which is characterized in that the hole of full carbon film It can be adjusted by the additive amount of graphene.
7. a kind of method as described in claim 1 preparation without the support full carbon film of active carbon, which is characterized in that be by active carbon Basic material, graphene connect to form the full carbon film of active carbon as crosslinking agent.
CN201610734288.4A 2016-08-25 2016-08-25 It is a kind of without support full carbon film of active carbon and its preparation method and application Active CN106345319B (en)

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CN201780003007.0A CN108136340A (en) 2016-08-25 2017-08-25 A kind of full carbon film based on activated carbon and its preparation method and application
PCT/CN2017/098964 WO2018036553A1 (en) 2016-08-25 2017-08-25 All-carbon film based on activated carbon and preparation method and use thereof
US16/328,205 US20190176096A1 (en) 2016-08-25 2017-08-25 All-Carbon Film Based On Activated Carbon And Preparation Method And Use Thereof

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CN106345319B (en) * 2016-08-25 2019-05-17 浙江大学 It is a kind of without support full carbon film of active carbon and its preparation method and application
CN109985534B (en) * 2017-12-30 2021-08-10 浙江大学 Pure active carbon filtering membrane and preparation method and application thereof
CN108579452A (en) * 2018-06-15 2018-09-28 南京水杯子科技股份有限公司 A kind of compound carbon membrane of graphene oxide and preparation method thereof
CN109126284B (en) * 2018-09-30 2019-10-25 江南大学 A kind of preparation method of graphene modified polypropene composite filtering material
CN110372109A (en) * 2019-06-25 2019-10-25 南通强生石墨烯科技有限公司 A kind of graphene scale inhibition filter core and preparation method thereof
CN110860215B (en) * 2019-10-12 2020-12-08 浙江大学 Graphene oxide film with tent-like structure and preparation method and application thereof
CN112642308A (en) * 2019-12-03 2021-04-13 贵州省材料技术创新基地 Polysulfone-biochar blending separation membrane and preparation method thereof

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